Catalyst and method for the removal of nitrogen oxides

Abstract: A catalyst for reducing nitrogen oxides into nitrogen and water in the presence of a reducing agent, which comprises: (a) titanium; (b) at least one element selected from the group consisting of tungsten and molybdenum in a total amount of 10-25% by weight in terms of oxides; and (c) niobium in an amount of 0.1-2% by weight in terms of oxides.

Description: This invention relates to a catalyst and a method for reducing nitrogen oxides contained in waste gases such as combustion waste gases or waste gases from chemical plants in the presence of a reducing agent such as ammonia. More particularly, the invention relates to a catalyst and a method for reducing nitrogen oxides stably and effectively into nitrogen and water over a long period of time even at a temperature as high as more than about 500°C Nitrogen oxides are contained in combustion waste gases from boilers, heating furnaces, gas turbines or diesel engines or waste gases from chemical plants for products such as nitric acid. The nitrogen oxides are noxious and it is necessary to remove the oxides from the waste gases. Thus, a denitrizing process has been put to practical use wherein the waste gas is contacted with a catalyst in the presence of, for example, ammonia as a reducing agent. A number of catalysts have been proposed and put to practical use heretofor; however, all the known catalysts have effective activity for reduction of nitrogen oxides only at a relatively low temperature. There has been found no catalyst which has high and stable activity over a wide range of temperatures, low to high, such as more than 500°C, for a long period. However, such a catalyst is in fact needed in some fields of denitrization. For instance, when a gas turbine or diesel engine is started, the resultant exhaust gas rapidly reaches a high temperature, and such a catalyst as above mentioned is needed to denitrize such an exhaust gas effectively and stably. It is already known that a catalyst mainly composed of titanium and tungsten is fairly resistant to heat, as disclosed in Japanese Patent Publication No. 52-35342. However, the catalyst is found to have low activity at low temperature, and moreover it is found not to have stable activity over a long period. A catalyst of titanium and vanadium is known, as disclosed in Japanese Patent Publication No. 54-2912, and a catalyst of titanium, tugsten and vanadium is also known, as disclosed in Japanese Patent Application Laid-open No. 50-128681. These catalysts have fairly good reduction activity for nitrogen oxides at low temperature; however, they are found not to have stable activity at high temperature. A further catalyst is known which contains at least one element selected from titanium, copper, chromium, tungsten, molybdenum, iron and nickel, in addition to vanadium and niobium, as disclosed in Japanese Patent Application Laid-open No. 51-87485. This catalyst is also found not to have stable activity at high temperature. The EP-A-0317875 discloses a catalyst comprising oxides of Ti, W, Mo and Nb. The invention provides a catalyst for reducing nitrogen oxides to nitrogen and water in the presence of ammonia as a reducing agent, which consists essentially of: (a) titanium dioxide; (b) at least one oxide selected from tungsten and molybdenum oxides in a total amount of 12-21% by weight; (c) niobium oxide in an amount of 0.15-0.5% by weight; and (d) optionally silica or zirconiun oxide. For use, any one or more or all of these components is or are preferably in compound (usually oxide) form. The titanium content of the catalyst in terms of oxides is preferably at least 50 wt.%, most preferably at least 70 wt.%, and may be the whole balance of the catalyst. Si and/or Zr may be present, in a total amount in terms of oxides which is preferably at most 30 wt.% (more preferably at most 25 wt.%) of the catalyst. The presence of a V component is preferably avoided. The nitrogen oxides include dinitrogen oxide, nitrogen monoxide, dinitrogen trioxide, nitrogen dioxide and dinitrogen pentoxide. The catalyst of the invention contains (a) titanium as a main component usually in the form of titanium dioxide, and in addition, (b) at least one element selected from the group consisting of tungsten and molybdenum in a total amount of 10-25%, preferably in the range of 12-21% by weight, in terms of oxides (e.g. WO 3 or MoO 3 ). These components are useful to improve heat resistance of the catalyst. The catalyst of the invention further contains niobium in an amount of 0.15-0.5% by weight, in terms of oxides (e.g. Nb 2 O 5 ). The niobium is useful to improve the activity for reducing nitrogen oxides at low temperature without adversely affecting the activity at high temperature. It is preferred that the catalyst contains all the elements (titanium, tungsten and/or molybdenum; and niobium) in the form of oxides. The catalyst of the invention way further contain silicon or zirconium, preferably as silica or zirconia. For the production of catalyst of the invention, any compounds of the elements may be used as raw materials. For the titanium component, titanium dioxide is preferably used; however, titanic acid, titanium hydroxide, titanium sulfate or composite Ti/Si oxides may be used, if necessary or desired. The composite oxides of titanium and silicon may be produced by, for example, admixing a titanium salt such as titanium sulfate with silica sol to prepare a mixture, adding alkali such as ammonia to the mixture to form a precipitate of mixed oxides, washing and drying the mixture of oxides, and then calcining the mixture of oxides at a temperature of 150-850°C. When titanium dioxide is used as a titanium component, it can be produced as follows - titanium sulfate is recovered as an intermediate from the production process of titanium dioxide by the sulfuric acid process, neutralized with ammonia, dried, and then calcined. However, if necessary, any titanium dioxide may be used irrespective of the method by which it is produced. With regard to a tungsten component, tungsten oxide, ammonium paratungstate or ammonium metatungstate is usually preferred, while with regard to a molybdenum component, molybdenum oxide or ammonium paramolybdate is usually preferred. With regard to a niobium component, chlorides are preferably used. The catalyst of the invention may be produced in any conventional manner known in the art. For instance, the catalyst may be produced by admixing the individual oxides of the elements and calcining the mixture; forming a coprecipitate of the oxides and calcining the coprecipitate; admixing at least one element oxide with water soluble salt(s) of the other element(s), kneading the mixture, and calcining the mixture; coating the oxides on a support or a carrier material; or by any combination of these methods. By way of example, titanium sulfate is admixed with niobium chloride, alkali is added to the mixture to form a coprecipitate, and the coprecipitate is dried and calcined to provide a mixture of titanium dioxide and niobium oxide. A solution of ammonium metatungstate is then added to the mixture of the oxides, and the resultant mixture is kneaded, molded to a green mold of a desired shape, and then dried and calcined to provide a molded catalyst. The catalyst of the invention may be formed into a molded catalyst of any shape, such as a honeycomb structure, pellet or granulate depending upon the use, if necessary by use of a molding assistant such as a polyvinyl alcohol binder, or the molded catalyst way be reinforced with an inorganic fiber reinforcement. Further, the catalyst may be supported on a support or a carrier material composed of, for instance, silica, alumina, magnesia or zirconia, or a mixture of these, as known in the art. The catalyst of the invention has high and stable activity for reducing nitrogen oxides over a wide range of low temperatures to high temperatures, more than 500°C, and is durable. The invention also provides a method of reducing nitrogen oxides contained in a waste gas to nitrogen and water in the presence of ammonia as reducing agent, which comprises contacting the waste gas with the catalyst as set forth hereinbefore at a temperature of greater than 500°C to not more than 600°C. The reducing agent is suitably used in an amount of 1-10 times, preferably 1-2 times, as much as the stoichiometric amount needed to completely react with the nitrogen oxides in the waste gas. The waste gas is suitably mixed with the reducing gas and then contacted with the catalyst fitted in a reactor at a space velocity (NTP) of 2000-100000 per hour, preferably 5000-60000 per hour, According to the invention, if the reaction temperature varies in the range from more than 500°C to not more than 600°C, the nitrogen oxides can be stably and effectively decomposed over a long period. The catalyst and method of the invention are accordingly suitable for use where a waste gas reaches a high temperature such as 500-600°C eventually or accidentally during the denitrizing reaction of waste gases. The reaction is usually carried out under normal pressure by a fixed bed process or, if necessary or desired, at increased pressure, e.g. up to about 10 kg/cm 2 , by a moving bed process or a fludizing bed process. The method of the invention is applicable to waste gases from sources such as power boilers or waste combustion furnaces among others, but is not limited to these. The invention will be more easily understood from reference to the following Examples. The Examples are intended to illustrate the invention only and are not to be construed as limiting the scope of the invention. Example 1 An amount of 940 ml of ethanol solution of niobium chloride (NbCl 5 ) containing niobium in an amount of 50 g/l in terms of Nb 2 O 5 was added to 200 liters of solution of titanium sulfate containing titanium in an amount of 100 g/l in terms of TiO 2 (obtained as an intermediate from the production of titanium oxide by the sulfuric acid process), and the mixture was then neutralized with ammonia water. The resultant precipitate was collected by filtration, washed with water, dried at 120°C for 12 hours, and then calcined at 500°C for 3 hours, to provide a mixture of titanium dioxide and niobium oxide. The mixture of the oxides was pulverized and adjusted to a suitable particle size. An amount of 7.1 kg of solution of ammonium metatungstate containing tungsten in an amount of 50% by weight in terms of WO 3 was added to the mixture of the oxides. The resultant mixture was kneaded and then extruded into a grid-like honeycomb mold having a pitch of 4.2 mm by use of an extruder. The mold was dried at 110°C and then calcined at 600°C for 3 hours, to provide a catalyst containing 15% by weight of tungsten in terms of tungsten oxide (WO 3 ) and 0.2% by weight of niobium in terms of niobium oxide (Nb 2 O 5 ). Example 2 An amount of 2.37 liters of ethanol solution of niobium chloride (NbCl 5 ) containing niobium in an amount of 50 g/l in terms of Nb 2 O 5 was added to 200 liters of the same solution of titanium sulfate as in Example 1, and the mixture was thermally hydrolyzed at 95°C. The resultant precipitate was collected by filtration, washed with water, dried at 120°C for 12 hours, and then calcined at 500°C for 3 hours, to provide a mixture of titanium dioxide and niobium oxide. The mixture of the oxides was pulverized and adjusted to a suitable particle size. An amount of 7.1 kg of solution of ammonium metatungstate containing tungsten in an amount of 50% by weight in terms of WO 3 was added to the mixture of the oxides. The resultant mixture was kneaded and then extruded into a grid-like honeycomb mold having a pitch of 4.2 mm by use of an extruder. The mold was dried at 110°C and then calcined at 600°C for 3 hours, to provide a catalyst containing 15% by weight of tungsten in terms of tungsten oxide (WO 3 ) and 0.5% by weight of niobium in terms of niobium oxide (Nb 2 O 5 ). Example 3 An amount of 8.9 liters of solution of ammonium paramolybdate containing molybdenum in an amount of 400 g/l in terms of MoO 3 was used in lieu of the solution of ammonium metatungstate, and otherwise in the same manner as in Example 1 there was prepared a catalyst containing 15% by weight of molybdenum in terms of molybdenum oxide (MoO 3 ) and 0.2% by weight of niobium in terms of niobium oxide (Nb 2 O 5 ). Comparative Example 1 The same solution of titanium sulfate as in Example 1 was neutralized with ammonia water. Otherwise in the same manner as in Example 1 there was prepared a catalyst containing 15% by weight of tungsten in terms of tungsten oxide (WO 3 ). Comparative Example 2 The same solution of titanium sulfate as in Example 2 was neutralized with ammonia water. Otherwise in the same manner as in Example 2 there was prepared a catalyst containing 15% by weight of tungsten in terms of tungsten oxide (WO 3 ). Comparative Example 3 An amount of 7.2 kg of solution of ammonium metatungstate containing tungsten in an amount of 50% by weight in terms of WO 3 and 1.6 liters of oxalic acid solution of ammonium metavanadate containing vanadium in an amount of 150 g/l in terms of vanadium pentoxide (V 2 O 5 ) (i.e., 240 g of vanadium in the solution in terms of V 2 O 5 ) were used in lieu of 7.1 kg of solution of ammonium metatungstate, and otherwise in the same manner as in Example 2 there was prepared a catalyst containing 15% by weight of tungsten in terms of tungsten oxide (WO 3 ), 1% by weight of vanadium in terms of vanadium pentoxide (V 2 O 5 ) and 0.5% by weight of niobium in terms of niobium pentoxide (Nb 2 O 5 ). Comparative Example 4 An amount of 3.5 kg of solution of ammonium metatungstate containing tungsten in an amount of 50% by weight in terms of WO 3 was used, and otherwise in the same manner as in Example 1 there was prepared a catalyst containing 8% by weight of tungsten in terms of tungsten oxide (WO 3 ) and 0.2% by weight of niobium in terms of niobium pentoxide (Nb 2 O 5 ). Comparative Example 5 An amount of 30.8 liters of ethanol solution of niobium chloride (NbCl 5 ) containing niobium in an amount of 50 g/l in terms of Nb 2 O 5 and 18.5 kg of solution of ammonium metatungstate containing tungsten in an amount of 50% by weight in terms of WO 3 was used, and otherwise in the same manner as in Example 1 there was prepared a catalyst containing 30% by weight of tungsten in terms of tungsten oxide (WO 3 ) and 5% by weight of niobium in terms of niobium pentoxide (Nb 2 O 5 ). Catalytic Reduction of Nitrogen Oxides The thus prepared catalysts were subjected to measurement of activity for reduction of nitrogen oxides (NOx). The catalyst was fitted in a reactor and contacted with a gas mixture at a temperature of 270°C or 530°C at a space velocity of 7950 per hr. and at a superficial gas velocity of 2.46 Nm/sec. Nitrogen oxides: 65 ppm Ammonia: 65 ppm Water vapor: 7 % Oxygen: 14.7 % Nitrogen: Balance The results are indicated in Table 1 in which the denitrizing rate is defined by ((NOx concentration at the inlet of reactor) - (NOx concentration at the outlet of the reactor)/(NOx concentration at the inlet of reactor)) x 100 (%). The denitrizing rate was measured at the initial stage of the reaction. Denitrizing Rate (%) 270°C 530°C Example 1 90.0 92.0 2 90.3 92.1 3 90.9 91.9 Comparative Example 1 85.1 90.9 2 87.0 91.1 3 93.7 75.3 4 88.0 89.6 5 92.5 80.8 As indicated in Table 1, the catalyst of the invention has an effective activity for reduction of nitrogen oxides over a wide range of temperatures, and even at a temperature as high as more than 500°C. After the above measurement, the catalyst was taken out of the reactor and then heated in an electric oven at a temperature more than 500°C over a period of 6000 hours. The catalyst was then again fitted in the reactor and was then contacted with the same gas mixture as hereinbefore, and the denitrizing rate was measured at the initial stage of the reaction. The results are indicated in Table 2. Denitrizing Rate (%) 270°C 530°C Example 1 89.8 89.6 2 90.1 89.8 3 90.0 89.9 Comparative Example 1 79.8 83.0 2 80.4 83.6 3 82.7 50.3 4 81.1 77.1 5 84.3 71.2 As indicated in Table 2, the catalyst of the invention has an effective and stable activity for reduction of nitrogen oxides at a high temperature more than 500°C for a long period.

Claims: A catalyst for reducing nitrogen oxides to nitrogen and water in the presence of ammonia as a reducing agent, which consists essentially of: (a) titanium dioxide; (b) at least one oxide selected from tungsten and molybdenum oxides in a total amount of 12-21% by weight; (c) niobium oxide in an amount of 0.15-0.5% by weight; and (d) optionally silica or zirconium oxide. A catalyst as claimed in claim 1 wherein (b) is tungsten oxide. A method for reducing nitrogen oxides contained in a waste gas to nitrogen and water in the presence of ammonia as a reducing agent, which comprises contacting the waste gas with a catalyst consisting essentially of: (a) titanium dioxide; (b) at least one oxide selected from tungsten and molybdenum oxides in a total amount of 12-21% by weight; (c) niobium oxide in an amount of 0.15-0.5%, by weight; and (d) optionally silica or zirconium oxide, at a temperature greater than 500°C to a temperature of not more than 600°C. A method as claimed in claim 3 wherein (b) is tungsten oxide.

Inventors: RIKIMARU HIROAKI, UMABA TOSHIKATSU, YOSHIKAWA YOSHIYUKI, RIKIMARU, HIROAKI, UMABA, TOSHIKATSU, YOSHIKAWA, YOSHIYUKI
Applicants: MITSUBISHI HEAVY IND LTD, SAKAI CHEMICAL INDUSTRY CO, MITSUBISHI JUKOGYO KABUSHIKI KAISHA, SAKAI CHEMICAL INDUSTRY CO., LTD.,
Application year: 1994
Main classification: B01D53
IPC codes: B01J23, B01D53